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summary of responses to the consultation Plastic packaging tax: July 2019

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Page 1: Plastic packaging tax - gov.uk · 1.2 Plastic packaging is typically only used for a short period and then disposed of, and accounts for 44% of plastic used in the UK,1 but 67% of

summary of responses to the consultation

Plastic packaging tax:

July 2019

Page 2: Plastic packaging tax - gov.uk · 1.2 Plastic packaging is typically only used for a short period and then disposed of, and accounts for 44% of plastic used in the UK,1 but 67% of
Page 3: Plastic packaging tax - gov.uk · 1.2 Plastic packaging is typically only used for a short period and then disposed of, and accounts for 44% of plastic used in the UK,1 but 67% of

summary of responses to the consultation

Plastic packaging tax:

July 2019

Page 4: Plastic packaging tax - gov.uk · 1.2 Plastic packaging is typically only used for a short period and then disposed of, and accounts for 44% of plastic used in the UK,1 but 67% of

© Crown copyright 2019

This publication is licensed under the terms of the Open Government Licence v3.0 except

where otherwise stated. To view this licence, visit nationalarchives.gov.uk/doc/open-

government-licence/version/3 or write to the Information Policy Team, The National

Archives, Kew, London TW9 4DU, or email: [email protected].

Where we have identified any third party copyright information you will need to obtain

permission from the copyright holders concerned.

This publication is available at www.gov.uk/government/publications

Any enquiries regarding this publication should be sent to us at

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ISBN 978-1-912809-73-8

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Contents

Chapter 1 Introduction 2

Chapter 2 Plastic packaging within scope of the tax 5

Chapter 3 Driving recycled content 8

Chapter 4 Setting the tax rate 13

Chapter 5 Liability for the tax 14

Chapter 6 Treatment of exports 17

Chapter 7 Excluding small operators 19

Chapter 8 Registering and reporting 22

Chapter 9 Ensuring compliance 23

Chapter 10 Understanding commercial practices and assessing

other impacts

25

Chapter 11 Next steps 27

Annex A List of respondents 28

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Chapter 1

Introduction

1.1 In March 2018, the government launched a call for evidence on using the

tax system or charges to tackle single-use plastic waste. This received a

record 162,000 responses, highlighting the strong public interest in action in

this area.

1.2 Plastic packaging is typically only used for a short period and then disposed

of, and accounts for 44% of plastic used in the UK,1 but 67% of plastic

waste.2

1.3 Over 2 million tonnes of plastic packaging is used in the UK each year.3 The

vast majority of this is made from new, rather than recycled plastic. Using

new plastic typically has greater environmental impact: it requires

unnecessary resource extraction and processing, with higher energy use and

emissions than using recycled material. It also results in significant amounts

of additional plastic waste on the market, which is generally sent to landfill

or incinerated. The process of consuming recycled material drives the

recycling market and helps to reduce the rate at which plastic is sent for

waste treatment/disposal further down the waste hierarchy.

1.4 The government’s call for evidence highlighted that using recycled plastic is

often more expensive than using new plastic, despite its lower environmental

impacts. Significant variations in the price of new plastic over time can also

discourage businesses from committing to using recycled plastic instead of

new plastic in the long term. The government wants to encourage the

sustained use of more recycled plastic in the production of plastic packaging

to help tackle plastic waste. This will help to drive the treatment of plastic

waste up the waste hierarchy so that more plastic is recycled rather than

being sent to landfill or incineration, to improve resource productivity and

make more plastic waste a useful and valued resource.

1.5 At Budget 2018, the government announced its intention to introduce a

world-leading new tax on businesses that produce or import plastic

packaging which uses insufficient recycled content, taking effect from April

2022. The tax will be set at a rate that provides a clear economic incentive

for businesses to use recycled material in the production of plastic

packaging, which will create greater demand for this material and in turn

1 ‘The UK Plastics Industry: A Strategic Vision for Growth’, British Plastics Federation, 2016

2 ‘A Plastic Future, Plastic Consumption and Waste Management in the UK’, WWF, 2018

3 ‘Digest of Waste and Resources Statistics’, Defra, 2018

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stimulate increased levels of recycling and collection of plastic waste,

diverting it away from landfill or incineration.

1.6 Businesses will have until April 2022 to adapt their processes before the

introduction of the tax. This will give them some time to adjust their

behaviour and help them manage any costs they may face, while ensuring

action is still taken to tackle this problem.

1.7 Earlier this year, HM Treasury launched a consultation seeking views on the

initial proposed design for the tax, and this closed in May.

1.8 The tax will complement reformed Packaging Producer Responsibility

regulations, which were considered in a consultation published in parallel.

These reforms will encourage businesses to design and use plastic packaging

that is easier to recycle, and discourage the creation of plastic packaging

which is difficult to recycle, which will increase the supply of easier-to-recycle

plastic. The government believes that together, the tax and Packaging

Producer Responsibility regulations will provide business with the right

incentives to recognise the impact of their plastic packaging decisions and

drive the development of more sustainable packaging. The government also

believes that it is right to deliver the tax and the reformed regulations in

separate systems given their different objectives and the high level of

complexity any combined system would bring. However, the government will

continue to ensure that the tax complements the reforms to the Packaging

Producer Responsibility regulations.

1.9 The government will also seek to ensure that the tax complements the

proposals for consistent collection of waste in England and a potential

Deposit Return Scheme for drinks containers, also consulted on in parallel.

These proposals respectively aim to help households and businesses to more

easily separate waste for recycling and set minimum standards for local

authorities, increasing the supply of plastic waste for recycling, and to boost

recycling materials whilst concurrently reducing the amount of littering.

Engagement with the consultation 1.10 The government received 436 written responses to this consultation,

including 332 to the standard consultation and 104 to the condensed

version (for stakeholders who preferred to provide views on only the high-

level principles of the tax). These responses include 184 from companies and

their trade bodies as well as 16 responses on behalf of charities, social

enterprises and non-governmental organisations and 103 from other

organisations, including local government and public bodies, with the

remainder submitted by private individuals or community groups.

1.11 During the consultation period, the government engaged directly with over

200 organisations, including manufacturers, retailers, environmental

charities and other experts to discuss the consultation in more depth.

1.12 This document sets out a summary of responses to the consultation. The

number of responses means that this document can only provide a high-level

summary, but the government is grateful for the large volume of evidence

submitted, which will be used in developing the design of the plastic

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packaging tax over the coming months. At Budget 2019, the government

will set out the next steps related to the tax.

1.13 Chapters 2 to 10 of this document summarise the answers received to the

questions outlined in each section of the consultation, except for the ‘About

you’ section (Questions 1-5), and Chapter 11 outlines next steps.

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Chapter 2

Plastic packaging within scope of the tax

2.1 This section sought views on the government’s proposal for defining plastic,

packaging and plastic packaging. To ensure the tax is clear and simple for

businesses and minimises administrative burdens, the government’s

preferred approach outlined in the consultation was to draw upon existing

definitions to set the scope, unless there are good reasons to do otherwise.

This includes plastic as defined by European Union regulations and

packaging as defined in the Packaging Producer Responsibility system.

Question 6 - Do you agree with the government’s suggested approach to defining plastic in scope of the tax?

Question 7 - Do you agree with the government’s suggested approach to defining packaging and packaging materials in scope of the tax?

Question 8 - Is the government’s approach to components of plastic packaging consistent with the way businesses operate and packaging is created?

Question 9 - Which of the above options for defining plastic packaging for composite material items do you think works better for the purposes of the tax?

Question 10 - Do you think alignment with the reformed Packaging Producer Responsibility regulations is important for the purposes of the tax?

Defining plastic in scope 2.2 The vast majority of respondents to Question 6 agreed with the

government’s suggested approach of defining plastic in line with European

Union (EU) regulations, with a small number disagreeing. Of those who

agreed, the majority focused on the benefits of aligning with this legislation.

2.3 Respondents mainly focused on the inclusion of bio-based, biodegradable

and compostable plastic within the definition. It was suggested that the

government’s position on these materials in the tax should remain under

review as further evidence emerges, with one stakeholder advocating for

them to be reviewed alongside the development of the Bioeconomy

strategy.4 Some respondents noted that there may be specific applications in

which compostable plastics may be beneficial, but also that the

infrastructure for dealing with these was not sufficiently developed.

2.4 Respondents also expressed views on synthetic and natural polymers and

mixed material packaging. Some environmental groups suggested that the

4 ‘Bioeconomy strategy: 2018 to 2030’, BEIS, 2018

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definition should cover all synthetic polymeric substances and some

businesses noted the need to distinguish between organic synthetic and

semi-synthetic polymers, whilst a few respondents highlighted the need for a

clearer definition of natural polymers. A small number of respondents

suggested that the government should instead look to use the definition of

polymer rather than plastic, as set out in other areas, such as in the EU

REACH regulations (relating to Registration, Evaluation, Authorisation and

restriction of Chemicals), given the scope of each definition.

Defining packaging and packaging materials in scope 2.5 The vast majority of respondents to Question 7 agreed with the

government’s suggested approach of defining packaging in scope to be

consistent with the reformed Packaging Producer Responsibility system, with

just a small number disagreeing. Those who agreed highlighted the benefit

of aligning definitions with those at the EU level, though it was noted that

these were currently under review. Certain stakeholders also noted the desire

to align these definitions across all government policies, and those co-

ordinated by industry, such as the UK Plastics Pact.

2.6 Several stakeholders raised concerns that there needed to be greater clarity

in the approach to composite packaging. There were mixed views from

stakeholders as to the treatment of reusable packaging, with some

advocating for their inclusion, and others suggesting the opposite as they

are designed to fulfil a role deemed more environmentally friendly by the

waste hierarchy.

Approach to components of packaging 2.7 Over half of respondents to Question 8 agreed with the government’s

approach of treating components of packaging that can be easily separated

as individual items of packaging, with a small number disagreeing. The

proposed approach was seen as being consistent with how businesses

operate and how packaging is created.

2.8 Of those who disagreed with the approach, it was noted that for packaging

components that are made of particular polymers, it might be harder to

incorporate recycled content. Some respondents suggested calculating the

level of recycled content as an average across the finished packaging

product, rather than on a component basis. It was also noted that some

businesses early in the supply chain might not know the composition of the

final packaging product given a number of businesses might be involved in

the process. Some respondents raised concerns with the definition of a

component being easily separable by hand.

Defining plastic packaging for composite material items 2.9 The consultation set out two options in Question 9 for the treatment of

composite packaging, which is packaging made of two or more different

types of material that cannot be separated by hand. Over a third of

respondents opted for Option 2, which would apply the tax to any

packaging which contains plastic, but only be charged on the weight of the

plastic content of the packaging. The reasoning given focused on capturing

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as much plastic packaging as possible, and avoiding encouraging composite

packaging. One environmental group suggested that composite packaging

which has a demonstrably larger carbon benefit should not be within scope.

However, other respondents argued that even for examples where this is

true, the lack of infrastructure to deal with these types of packaging at end

of life conflicts with circular economy principles, which they deemed to be

more important.

2.10 Over a third of respondents were evenly split between the option of

alignment with the existing Packaging Producer Responsibility regulations,

which would apply the tax to all packaging that is predominantly plastic by

weight, and Option 1, which would set a fixed percentage of plastic content

required for packaging to be considered as plastic packaging. Stakeholders

advocating for alignment noted that this would be the easiest for businesses

to administer and hence minimise burdens placed on them to comply with

the tax. Certain stakeholders advocating for Option 1 noted that this would

be more equitable and prevent bringing particular unrelated packaging

products into scope, such as cans with polymeric linings.

2.11 A small number of respondents advocated for another option, with the

majority suggesting that the government align with the Confederation of

Paper Industries’ guidelines which seek to restrict plastic content to a

maximum of 5% of pack weight, with an industry preference for no more

than 3%.

Alignment with the reformed Packaging Producer Responsibility regulations 2.12 Over three-quarters of respondents to Question 10 agreed that alignment

with the reformed Packaging Producer Responsibility regulations was

important for the purposes of the tax, with a very small number disagreeing.

Some of the reasons for disagreement were that a weight-based metric is

not the best approach, or that there might be confusion if mixed material

packaging was treated differently in the two systems.

2.13 More widely, regarding the choice of having a tax, some respondents

believed that using modulated fees within the reformed Packaging Producer

Responsibility system would be a simpler and fairer way to encourage the

right behaviours in terms of using recycled content.

Government response 2.14 The government notes the levels of support for the proposed approach set

out in the consultation document. The government will consider further the

most appropriate definitions for plastic and for packaging, in particular

regarding the treatment of bio-based, biodegradable and compostable

plastic. The government will also consider further how composite packaging

will be treated within the scope of the tax, given the focus on improving

environmental outcomes. The government will continue to ensure policies

are designed to be complementary, taking into consideration the

development of the Packaging Producer Responsibility reforms in the design

of the tax.

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Chapter 3

Driving recycled content

3.1 This section sought views on the government’s proposed approach to

defining recycled content and the threshold for the purposes of the tax. The

consultation outlined the government’s preferred option of setting a single

threshold at 30% recycled content with a definition drawing on the

International Organisation of Standardisation (ISO) standard 14021, which

can include some pre-consumer and post-consumer material, whether

mechanically or chemically recycled.

Question 11 - Do you agree with the government’s suggested approach to defining recycled content for the purposes of the tax?

Question 12 - Are there any environmental or technical reasons to consider excluding any particular ways of recycling plastic?

Question 13 - Is there any way that the proposed approach to defining recycled content could encourage unintended consequences, such as wasteful manufacturing processes?

Question 14 - Do you agree with the government’s preferred approach of a single threshold, and why? If not, what alternative would be better, and what are the risks associated with this? Please explain your answer and provide any supporting information and evidence.

Question 15 - Assuming a single threshold, do you agree with a 30% threshold for recycled content and why?

Question 16 - Are there any products for which it would be very challenging to increase the level of recycled content, and why? If so, please outline the effect of a tax on production decisions and consumption of these items.

Question 17 - Are there any products for which the use of recycled plastic is directly prohibited in packaging? If yes, please provide details on these products stating the relevant legislation and industry standards as well as the effect of a tax on production decisions and consumption of these items.

Question 18 - What evidence is currently held by liable manufacturers and importers on the levels of recycled content in their plastic packaging and how it might be able to meet the requirements of identifying recycled content levels?

Question 19 - If you are an importer of unfilled plastic packaging or plastic packaging material, what information do you hold on the recycled content? What controls or

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assurance do you have over the accuracy of this information? How might you influence the level of recycled plastic content?

Defining recycled content 3.2 Around two thirds of respondents to Question 11 agreed with the

government’s suggested approach of drawing on ISO standard 14021:2016

to define recycled content, whilst a small number were opposed. Those who

agreed thought it was helpful to align with existing frameworks, whilst some

respondents also highlighted that the European Commission is developing its

own definition which it could be helpful to align with.

3.3 Some respondents thought it was important to include any method of

recycling to encourage as much recycling and use of recycled material as

possible. Several respondents argued that the definition should ensure

‘feedstock’ and ‘chemical’ recycling is accommodated, whilst others noted

that this process was still at an early stage of development and that there

could be challenges with assessing plastics that have been reprocessed

through chemical recycling rather than other processes as they have similar

chemical compositions. Some respondents suggested that new recycling

processes should be assessed for their overall environmental impact.

3.4 Some respondents suggested that including some forms of pre-consumer

waste in the definition of recycled content could encourage wasteful

manufacturing processes to generate more waste, whilst others said that the

increased cost of wasteful processes would discourage this. Some local

authorities sought reassurances that the inclusion of pre-consumer plastics

will not hinder the development of end markets for post-consumer plastics.

3.5 Some food packaging manufacturers argued that scrap and regrind should

be included in a definition of recycled content as this is a source they

currently use for packaging.

3.6 Some respondents suggested that the proposed definition of recycled

content does not take into consideration compostable plastics. One

respondent noted that these plastics are at least in part plant based and so

the equivalent of recycled content for them would be from renewable

carbon sources.

Setting a single threshold 3.7 Over a third of respondents to Question 14 agreed with the government’s

preferred approach of a single threshold. Conversely, just under half

preferred the alternative options set out in the consultation, including a

small minority explicitly asking for multiple thresholds (Option 1) and a very

small minority opting for different thresholds for different types of products

(Option 2).

3.8 Most waste managers and local authorities agreed with a single threshold.

The reasons most frequently cited to justify this support was that it would be

the simplest option for businesses to administer, minimising non-compliance

risks and sending “a clear and unambiguous message in a way that a more

complicated system might not”.

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3.9 A large majority of packaging manufacturers, retailers, and environmental

groups thought that the alternative proposals set out in the consultation

were more advisable. The main reason given was that these alternatives

could drive greater behavioural change across more of the industry. Some

other respondents suggested that multiple thresholds could also include an

incentive to go beyond 30% recycled content. Those who favoured multiple

thresholds also thought this could allow for different approaches to different

types of plastics depending on the current availability of recycled material by

plastic, which could reduce the incentive to change between plastic types.

Threshold level 3.10 Just under half of the respondents to Question 15 disagreed with the

proposal for a 30% threshold for recycled content, whilst around a third

thought it was appropriate.

3.11 Some of those who agreed with a 30% threshold believed it was a “clearly

defined and memorable stretch target that can be understood by

consumers, converters and those through the supply chain”. These

respondents also thought that it was helpful to use a target in the same

range as the UK Plastics Pact and the EU Single-Use Plastic Directive.

3.12 The majority of those who explained why they disagreed with the proposal

wanted the threshold to be more ambitious given that some brands and

retailers have already pledged to reach an average of 30% recycled content

across all their plastic packaging by 2025 through the UK Plastics Pact. Some

respondents suggested that the date of introduction should be earlier than

2022. Packaging manufacturers mainly wanted the threshold to be lower

due to concerns that businesses far from reaching the threshold would be

discouraged from increasing the recycled content within their packaging.

They also noted that they thought there will be a limited supply of recycled

content in the short term which would make it challenging to meet the 30%

target and suggested that it should be introduced in 2025 instead of 2022

to align with the UK Plastics Pact. Some respondents suggested that a later

date of introduction could mean there would be more availability of recycled

content, following the reforms to the Packaging Producer Responsibility

regulations.

3.13 Many respondents were keen that government reviews the threshold level

regularly to ensure it remains at an appropriate level in the context of

developing recycling facilities and technical innovation.

Products where it is challenging or prohibited to use recycled content 3.14 In the consultation, the government requested information on any products

where it would be very challenging to increase the level of recycled content

or where the use of recycled plastic is directly prohibited in packaging.

3.15 Many respondents to Question 16 and 17 stated that for some plastic types

and packaging products, it would be challenging or currently not possible to

increase recycled content because of technical, regulatory or supply

limitations. Packaging destined for some food contact and medical purposes

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were the most frequently cited examples of such products. Recycled material

in food contact packaging requires regulatory approval that the recycling

process is to a food safe standard. Many respondents noted that this

approval is currently given for a limited number of plastics, such as

polyethylene terephthalate (PET) and high-density polyethylene (HDPE).

Other respondents highlighted that the packaging of medical products

requires additional testing of the performance of the packaging to secure

the necessary regulatory approval to bring such products to market.

3.16 A number of businesses outlined the technical challenges they face when

trying to increase recycled content levels in thin flexible films or when

needing to maintain certain packaging characteristics for specific

applications, such as strength where there are health and safety implications.

Other respondents also noted that the government should consider the

limitations for packaging used for the transportation of hazardous goods,

toys and cosmetics.

Evidence held by liable manufacturers and importers 3.17 In the consultation, the government requested information on the evidence

currently held by liable manufacturers and importers on the levels of recycled

content in their plastic packaging and how it might be able to meet the

requirements identifying recycled content levels.

3.18 Many of those who responded to Question 18 acknowledged that the

manufacturers held the information on the levels of recycled content and

that in some cases this was currently supplied to the purchasers and further

along the supply chain, with some operators conducting audits on their

suppliers’ claims. Some respondents highlighted that this oversight of

information on recycled content was more common in larger companies and

those signed up to the UK Plastics Pact. A substantial number of respondents

suggested that recyclers and manufacturers would need to be audited to

ensure compliance, such as by an approved third party against an

appropriate international standard.

3.19 Several respondents also outlined that there is currently no consistent

method of measuring recycled content in packaging, which constrains the

information held on current levels of recycled content. Some suggested a

‘mass balance’ approach to calculating levels of recycled content, which

involves the use of a weight-based formula that sets out how the inputs to a

product or products relate to the amount of recycled content as a share of

the total mass of the packaging.

3.20 On the importation of plastic packaging, many respondents to Question 19

thought it would be challenging to verify the recycled content against UK

specific regulations. Some respondents highlighted that they did not

currently know where their materials originated from and many of those that

did said the reliability of information varied significantly depending on the

source of packaging, in part because of differences in definitions in non-

European countries. Other respondents noted that large businesses more

regularly audit suppliers to ensure they comply with specifications and

provide evidence of their declarations.

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Government response 3.21 The government notes the variety of views on the recycled content threshold

and will continue to consider which approach will best support the

objectives of the tax while minimising administrative burdens. The

government acknowledges that many respondents sent information on

products where they consider it could be challenging to increase the level of

recycled content and will consider this carefully in designing the tax. The

government recognises that businesses currently hold varying levels of

evidence on recycled content, also acknowledging the different views on

how it should be defined and the request for verification. The government

acknowledges views that both the tax should be introduced earlier than or

later than 2022. The government recognises the need to tackle this problem

as quickly as possible, which is why the tax will be introduced by 2022,

incentivising faster and wider action than voluntary initiatives whilst also

giving businesses time to adapt.

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Chapter 4

Setting the tax rate

4.1 This section sought views on the government’s proposal for charging the tax

at a flat rate per tonne of a product. The consultation outlined that charging

by weight aligns with the current Packaging Producer Responsibility

regulations and simplifies the administration of the tax.

Question 20 - Do you agree with the government’s suggested approach of setting a flat rate per tonne of a plastic packaging product? Why?

4.2 Two thirds of respondents to Question 20 agreed with the government’s

proposal of setting a flat rate per tonne of a plastic packaging product, and

a small number disagreed.

4.3 Those in favour agreed that a flat rate per tonne would be the simplest

option, making it easy for businesses to administer and for the government

to collect and monitor. Taking the same approach as the current Packaging

Producer Responsibility regulations and the proposals for reforming this

system was also viewed positively as it would make the tax easier to manage.

4.4 Packaging manufacturers were amongst those who were most against,

suggesting that charging by weight may lead to businesses being driven

towards using lighter materials that could be less recyclable and potentially

have higher environmental impacts. To solve this issue, an environmental

group suggested that the current method of charging per tonne of material

could be complemented by a per unit price.

4.5 Some respondents requested that the rate is aligned with oil price forecasts

and subsequent differences between the cost of new plastic and recycled

plastic to ensure there is always a financial incentive to use the latter.

4.6 Finally, a small number of respondents suggested a rate escalator, similar to

the landfill tax escalator where the rate is increased over time and where

these increases were known well in advance. Respondents said that this

could provide businesses with long-term visibility and help drive the demand

for recycled plastic material.

Government response 4.7 The government notes that the majority of respondents support its approach

of setting a flat rate per tonne of a plastic packaging product, but will

continue to consider which approach will best support the objectives of the

tax and is most administratively feasible.

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Chapter 5

Liability for the tax

5.1 This section sought views on who would be liable for the tax, including at

which point in the supply chain the tax is charged and which imports are in

scope of the tax. The consultation outlined the government’s proposal to tax

plastic packaging at the point of production or the importation of equivalent

products. The consultation also outlined that the government was

considering joint and several liability.

Question 21 - Do you agree with the proposed points at which domestic or imported products would be liable for the tax? If not, at what point in the supply chain do you think the tax point should be and why?

Question 22 - Are there any situations where the proposed tax points would be administratively, practically or legally difficult? Please explain any adaptions that might be necessary.

Question 23 - If you are a business that produces or imports plastic packaging, how much of your yearly production, in tonnes, would you expect to be liable for the tax?

Question 24 - Do you provide (manufacture or import) plastic material which could be used as packaging without knowing the final use of the product? Is this a common occurrence?

Question 25 - Would you support extending joint and several liability for UK production, and for imports?

Question 26 - Please outline any issues in relation to routine wastage or spillage that may have an impact on the tax liability.

Question 27 - Do you agree with the government’s initial proposal that the tax at import should only apply to unfilled packaging? If not, what would the effects be? What alternative would you prefer and how would it work?

Where the tax is charged domestically 5.2 A majority of respondents to Question 21 agreed with the government’s

proposal for the tax to apply domestically at the point of production, given

this is where the recycled content is added or is close to this point, whilst a

small number disagreed. There were mixed views on the best way to

approach situations where there is more than one domestic manufacturer of

packaging. Those who favoured Option 1, which would tax plastic

packaging when it is first commercially exploited, thought this would be

effective in driving behaviour change and the manufacturers would be well

placed to provide information on recycled content. Those in favour of Option

2, which would tax packaging at the point where it is commercially exploited

through sale or supply to be filled, packed or assembled, thought this would

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provide more clarity on when the tax would be due, certainty that the

taxable material would be packaging and more alignment with the approach

proposed for imported plastic packaging.

5.3 Some respondents suggested alternative tax points, including taxing at the

pack-filler stage or taxing brand owners and retailers. They highlighted that

this part of the supply chain often sets out requirements for the design of

the packaging, including the levels of recycled content, and tracks

information on packaging supplied to them. It was suggested these tax

points could be similar to some of the options being considered in the

planned reforms to the Packaging Producer Responsibility system. In

addition, respondents highlighted that pack-fillers, brand owners and

retailers often bring together many packaging components from different

suppliers (e.g. tub and lid or bottle, cap and label), so taxing them could

allow recycled content to be considered across packaging components rather

than on a component by component basis. Other respondents suggested

that there could be increased complexity from focusing on these alternative

points in the supply chain.

5.4 Few respondents to Question 22 expressed a view on whether they

anticipated any administrative, practical or legal difficulties with the

proposed tax points. However, some of those that did outline views

highlighted the administrative burden of recording additional information on

packaging, in particular on recycled content, and some suggested it was

important to clarify the exact point in the supply chain the tax would apply.

5.5 Only half of the respondents to Question 24 confirmed whether the final use

of the product was known or unknown at the point at which they provided

plastic material which could be used as packaging. The vast majority of those

that did express a view confirmed that the final use of the product was

known. Those who said that the final use was unknown included some

manufacturers of plastic film.

The scope of imports the tax applies to 5.6 The majority of respondents to Question 27 disagreed with the

government’s proposal not to include filled plastic packaging imports in

scope of the tax, whilst only a small minority were in favour. The most

common reason among those that disagreed was the potential negative

impact on the competitiveness of UK manufacturing, with many

commenting that businesses may be encouraged to fill plastic packaging

overseas in order to avoid the tax, disadvantaging UK producers or

manufacturers of plastic packaging. A number of respondents cited the large

amount of filled plastic packaging imported into the UK, noting that it may

undermine the environmental rationale of the tax to exclude a sizeable

proportion of plastic packaging placed on the UK market from the scope of

the tax. Several respondents gave examples of other unintended

environmental consequences linked to not including filled imports. These

included a continued preference for new plastic over recycled, alongside

possible harmful impacts linked to increased carbon emissions (for example,

through increased transportation of filled goods).

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5.7 The respondents who agreed with the initial proposal or who indicated

practical concerns highlighted the increased complexity of complying with

the tax that may arise from including filled imports. A concern was raised

that packaging from a very large number of suppliers would need to be

audited on a country by country basis to verify the level of recycled content,

which could create a disproportionate administrative burden and possibly

outweigh the amount of tax that would be due.

Details of how the tax is charged 5.8 The majority of respondents to Question 25 supported the government’s

proposal to extend joint and several liability to other businesses in the supply

chain for UK production and for imports, whilst only a small number

disagreed. Many respondents noted that this would help reduce levels of

avoidance and evasion and would align with the approach used in other tax

regimes. Some respondents suggested that this approach would increase the

administrative burden, as those who had joint and severable liability may be

several steps away from the initial taxpayer and would have to trace records

back.

5.9 Respondents to Question 26 mainly referred to routine wastage and spillage

occurring throughout the supply chain and that this wastage is often sent to

be recycled. Several respondents, including retailers, local authorities and

charities, suggested that this material should be within the scope of the tax

to ensure companies are incentivised to minimise their wastage. One large

retailer thought that the tax should be aligned with what manufacturers

procure rather than produce as it would encourage producers to be more

efficient and productive with their production processes and help reduce

waste. Other respondents suggested that the tax liability should be on the

final packaging product to exclude taxing wastage, as it is not commercially

exploited.

Government response 5.10 The government notes the majority support for charging the tax at the point

of production as well as suggestions for other points in the supply chain. The

government will continue to consider which approach will best support the

objectives of the tax and is most administratively feasible. The government

acknowledges the strong views in favour of including filled imports in scope

of the tax and will consider carefully the arguments made for inclusion. The

government also recognises the support for extending joint and several

liability to other businesses in the supply chain in a way which does not have

disproportionate administrative impact.

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Chapter 6

Treatment of exports

6.1 This section sought views on the government’s approach to treating exports

of chargeable plastic packaging. The consultation proposed that to ensure

UK manufacturers are not placed at a competitive disadvantage, directly

exported chargeable plastic packaging would not be liable for tax. Where

the tax is paid and the plastic packaging is subsequently exported, the

government proposed in the consultation that a credit would be restricted to

the original taxpayer and sought views on alternative options.

Question 28 - Do you agree with the government’s suggested approach for crediting exports?

Question 29 - Do you foresee any difficulties in providing appropriate records to demonstrate that packaging has been exported?

6.2 Over half of the respondents to Question 28 expressed a view on the

government’s suggested approach for crediting exports. Slightly more of

these respondents agreed than disagreed that exports should receive a tax

credit in order to maintain competitiveness in global markets. However,

many were concerned that the business that exports the packaging may be

different to the business that paid the tax, suggesting that if only the latter

could claim credits it would put some exporters at a disadvantage.

6.3 Conversely, other respondents took the view that the tax should be applied

to all plastic packaging regardless of its eventual destination to support the

environmental rationale and allow the UK to set a global example. Some

respondents thought that not taxing exports could lead to UK manufacturers

targeting the export market and not making the effort to incorporate

recycled content.

6.4 Few respondents to Question 29 expressed a view on the record keeping

requirements where packaging is exported. However, those that did outline

views did not foresee any difficulties providing appropriate records.

6.5 Several respondents outlined potential difficulties with the government’s

proposal to restrict credits to liable manufacturers when the exporter is not

the person that paid the tax, as commercial sensitivity could prevent the

exporter from passing the required records to the person that actually paid

the tax. Moreover, some respondents raised the additional administrative

burdens for businesses, except where they are already obligated under the

Packaging Producer Responsibility system, for which comprehensive records

are currently maintained.

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Government response 6.6 The government is clear that plastic packaging waste is a global problem and

is setting an example by introducing this world-leading new tax. The

government acknowledges that it is also important to ensure the tax does

not negatively affect the competitiveness of UK businesses that export plastic

packaging, especially where doing this could be detrimental to the

environment. The government will continue to consider which approach will

best support the objectives of the tax, is most administratively feasible and

does not have a disproportionate impact on business.

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Chapter 7

Excluding small operators

7.1 This section sought views on the government’s proposal to exclude the

smallest operators from the tax, via a minimum threshold (a ‘de minimis’),

which is common practice across other business tax regimes, including in

VAT. This would ensure that administrative burdens for taxpayers are not

disproportionate to the amount of tax that would be due, in situations

where operators are too small to have a material impact on demand for

recycled plastic.

Question 30 - Do you agree that the government should seek to exclude small operators? If yes, what would the risks be if the government did not do this?

Question 31 - Would Option 1a, Option 1b or Option 2 best meet the government’s objective of excluding small operators from the tax whilst ensuring the tax has a strong environmental rationale?

Question 32 - What factors should the government consider when setting a threshold (either on volume or turnover) or a relief? Do you have any suggestions for appropriate levels? If so, please provide an explanation for why you believe this is appropriate.

Question 33 - Would having a de minimis create any significant risks to the effectiveness of the tax at import (including, but not limited to, treatment of multiple imports from the same exporter/manufacturer/brand owner)? If yes, please provide evidence and suggest any additional legislative or operational countermeasures.

Question 34 - Do you anticipate any risks or issues that would arise from introducing a de minimis that are not explored above? Please provide details.

Whether to exclude small operators 7.2 Around a third of respondents to Question 30 agreed that the government

should seek to exclude small operators, whilst a similar number did not

agree and the rest did not express a view. Many in favour stated that the

financial and administrative burden on small businesses would be

disproportionate compared to the environmental benefits. One trade body

suggested their members would be much more concerned by this

administrative burden than by any increase in the cost of packaging and

goods given the former cannot be passed on.

7.3 Those not in favour thought that all operators should be liable for the tax to

maximise its impact, with many suggesting the de minimis should be set as

low as possible were it to be introduced. A small number of respondents

noted that while individual small operators may not use much packaging,

they might represent a large volume when taken as a group. Another

concern was that if imported filled packaging were brought into scope,

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there would be a disproportionate burden on the businesses liable to pay the

tax compared to those below the de minimis.

7.4 Many respondents believed the de minimis approach should be aligned with

the reforms to the Packaging Producer Responsibility regulations. A few local

authorities also suggested phasing in small operators at a later date, while

other respondents proposed a simplified scheme or flat fee for small

operators.

Approach to setting a de minimis threshold 7.5 The consultation set out three options in Question 31 for setting a de

minimis: i) threshold based on production/importation weight (Option 1a);

ii) threshold based on turnover and production/importation weight (Option

1b); and iii) universal relief on the first portion of chargeable products

(Option 2).

7.6 The respondents had mixed views on this question. Many local authorities

were in favour of Option 1a as the current Packaging Producer Responsibility

system considers tonnage, with a couple of respondents noting that it would

need to be based on aggregate tonnages to ensure smaller shipments do

not escape the tax. Around half of the respondents who chose Option 1b

made the same argument given the Packaging Producer Responsibility

system is tried and tested, and the turnover criteria would ensure an

operator had reached a reasonable size, both financially and in terms of

tonnage, before they are liable to pay the tax. Some respondents suggested

that the government would need to consider whether this approach applies

to total company turnover or just on plastic packaging items. They noted

that the latter could be difficult to isolate and so basing turnover on filed

company accounts could lead to measuring difficulties and unintended

consequences depending on the approach taken, especially when companies

restructure.

7.7 The respondents who chose Option 2 stated that it would support a level

playing field, with a few packaging manufacturers outlining that the option

could be developed to incentivise smaller companies to increase the recycled

content in their packaging. One respondent suggested this option could

incentivise all operators to produce some packaging without recycled

content, whilst another flagged that it would not allow businesses to

operate a consistent accounting practice across the year and would increase

the risk of errors as they would initially have to submit nil returns or none at

all until they reach the threshold.

7.8 A small number of respondents suggested a specific threshold, but those

that did stated that it should be lower than the current Packaging Producer

Responsibility system de minimis, with multi-tiered fees or using the VAT

threshold as options.

Government response 7.9 The government notes the mixed views on the proposal to exclude small

operators, that many respondents suggested any de minimis should be as

low as possible and that the government should consider alignment with the

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reforms to the Packaging Producer Responsibility regulations. The

government will continue to consider which approach will best support the

objectives of the tax, is most administratively feasible and does not have a

disproportionate impact on business.

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Chapter 8

Registering and reporting

8.1 This section sought views on the government’s proposal to require

registration and reporting on a “digital by default” basis, with similar

registration requirements to other taxes, and on the estimated costs for

taxpayers to meet their obligations.

Question 35 - Do you agree that the registration and reporting requirements outlined are appropriate? If not, please specify why.

Question 36 - Please provide details of the estimated one-off costs for registering with HMRC.

Question 37 - Please provide details of the expected one-off and on-going costs of completing, filing, and paying the return.

8.2 Around half of the respondents to Question 35 agreed that the registration

and reporting requirements outlined in the consultation were appropriate,

with some noting that it was helpful to be consistent with other HMRC

registration and reporting processes. Conversely, a very small number of

respondents disagreed and thought the requirements should be more

aligned with the Packaging Producer Responsibility system, including an

annual reporting period.

8.3 Some respondents noted that the government should consider group

registrations to make the requirements less burdensome for groups and that

it was important to allow sufficient time to prepare for the registration and

reporting requirements.

8.4 There were a range of views on costs of registering and reporting.

Respondents to Question 36 and 37 suggested the initial cost of developing

the reporting system and ongoing data gathering were likely to be more

substantial elements and costs may be reduced if reporting requirements

were similar to the Packaging Producer Responsibility system.

Government response 8.5 The government welcomes the general support for the proposals on

registration and reporting requirements and will continue to develop these

further, taking into account suggestions made in the consultation. The

government recognises that there will be costs associated with registering

and reporting and will seek to minimise these where possible. The

government also acknowledges that taxpayers will need to be given

sufficient time to prepare for the introduction of the tax.

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Chapter 9

Ensuring compliance

9.1 This section sought views on the government’s proposals to use similar

compliance powers to those already in place for other taxes, focusing on

HMRC’s compliance and enforcement powers, risks of non-compliance and

the approach to assuring the level of recycled content. The government

outlined in the consultation its proposal to align reporting requirements

closely with existing records where they are sufficient and that it would

consider additional measures that could help to ensure compliance.

Question 38 - Is the government’s suggested approach to compliance proportionate and appropriate? If not, please outline any scenarios that you anticipate may require bespoke compliance powers or penalties?

Question 39 - Are our anti-abuse proposals sufficient to tackle the risk of fragmentation (abuse of the de minimis or universal relief) from UK based plastic producers?

Question 40 - Is our approach regarding assuring the accuracy of declared recycled content appropriate? If not, please share any other suggestions you may have.

Question 41 - Do respondents believe that using UK based agents for non-established taxable persons may help support compliance?

Question 42 - Are there any further compliance risks that have not been addressed in this chapter, please provide details?

9.2 Around half of the respondents to Question 38 expressed a view on the

government’s suggested approach to compliance. The vast majority of those

that did thought the proposed approach to compliance was proportionate

and appropriate. Those who agreed suggested it was right to adopt similar

compliance powers to those already in place to administer other taxes and

duties. Those who disagreed noted the challenge of assuring the level of

recycled content and that it was important that the compliance approach

ensured a fair playing field in this area.

9.3 The majority of respondents who expressed a view on Question 39 on the

risks to fragmentation thought it was right to take steps to tackle potential

abuse, and that anti-fragmentation provisions together with a ‘connected

persons’ test should provide a proportionate solution. Those who disagreed

suggested that an alternative approach to reduce the risk of fragmentation

was to have no de minimis threshold.

9.4 The majority of respondents to Question 40 did not express a view on the

government’s approach to assuring the accuracy of declared recycled

content. Many of those that agreed businesses should be required to

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conduct due diligence and maintain records that show the levels of recycled

content suggested this would need to be supported by clear guidance and

sufficient monitoring and enforcement of non-compliance. Some

respondents suggested the approach needed to be strengthened, and this

could be done by the certification of recycled content to ensure traceability,

whilst recognising that this would likely be administratively burdensome.

Other respondents suggested that it would be helpful to have a consistent

way of calculating recycled content to limit the chance of inconsistent tax

treatment.

9.5 Whilst two-thirds of the respondents to Question 41 did not express a view,

substantially more respondents agreed than disagreed that using UK based

agents for non-established taxable persons may help support compliance,

with several noting that this approach would be in line with other tax

regimes. Those who disagreed highlighted the additional cost for business of

this approach and that UK based agents might be discouraged if they were

jointly and severally liable for the tax.

9.6 Some respondents raised further issues related to compliance, including the

importance of verifying the provenance of the recycled content to show it is

genuine and the communications related to the tax to ensure all businesses

are aware.

9.7 Some respondents expressed concerns that, were there to be a de minimis

threshold, this could incentivise deliberate gaming whereby businesses split

up to avoid being liable for the tax. This was highlighted as a particular risk

for imports, where overseas manufacturers and suppliers might distribute

their packaging through multiple small importers to come under a threshold.

Government response 9.8 The government welcomes the general support for the proposals on

ensuring compliance and will continue to develop these further, taking into

account suggestions made in the consultation. The government recognises

in particular the importance of assuring the levels of recycled content in a

consistent way and will ensure that robust requirements are set out to assure

the levels of recycled content.

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Chapter 10

Understanding commercial practices and assessing other impacts

10.1 These two sections sought information about how the plastic packaging

sector operates, including how it will be affected by the tax, and whether

there are any unintended impacts the government should consider that have

not previously been mentioned, especially adverse impacts on groups with

protected characteristics.

10.2 The government welcomes all the information received that will support

further policy development.

Impact on groups with protected characteristics 10.3 Local authorities suggested that if the tax regime creates any additional

burdens on them without receiving extra funding, there is risk that the tax

could have a negative impact on groups with protected characteristics as

local authorities may need to reduce spending on services that benefit these

groups.

10.4 Some respondents referred to increased costs for businesses which would be

passed on, at least in part, to the consumer. They suggested that this was

more likely in packaging where there are more challenges to include recycled

content, such as in medical or some food-contact applications, and that this

could disproportionately impact lower income groups.

10.5 A small number of respondents suggested the tax could have an impact on

older people or those with disabilities were it to lead to manufacturers

changing the materials used in packaging towards some which are harder to

open, such as canned products or glass jars. If the tax affects the ease of

opening medicine, such as blister packs, one respondent suggested the tax

could have an impact on groups with protected characteristics.

Other issues 10.6 Some respondents suggested that the government should consider spending

some or all of the revenue raised from the tax to support investment in the

waste management industry or wider environmental measures. Respondents

suggested that if instead of the tax the reforms to the Packaging Producer

Responsibility system included incentives for recycled content, then this could

mean the revenue raised would be reinvested in waste management.

10.7 Some respondents highlighted the importance of the tax applying across the

UK in a consistent manner. For example, one suggested that the tax would

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need to extend to Northern Ireland to avoid the risk of it becoming a place

where industry sell off remaining stocks of plastic products.

10.8 A few respondents suggested that the government should publish an

assessment of how much the tax will cost to design, implement and collect,

and that this needs to be more comprehensive than HMRC’s usual

compliance cost analysis.

Government response 10.9 The government will consider any potential impacts on lower income groups

or those with protected characteristics carefully in the design of the tax.

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Chapter 11

Next steps

11.1 The government welcomes the large number of responses received to the

consultation to inform the development of this world-leading new tax,

which will provide a clear economic incentive for businesses to use recycled

material in the production of plastic packaging. This tax will create greater

demand for recycled plastic, stimulating increased levels of collection and

recycling of plastic waste.

11.2 The government notes that many respondents agreed with the initial

proposals in the consultation document on many elements of the tax design,

including: definitions of plastic, packaging and recycled content; setting a

flat rate per tonne of plastic packaging; charging the tax domestically at the

point of production; how to treat exports; and proposals for registration,

reporting requirements and ensuring compliance.

11.3 The government also recognises that there were some areas where

significant numbers of respondents disagreed with the initial proposals set

out in the consultation. For example, the majority of respondents disagreed

with the government’s proposal to not include filled packaging imports, and

just under half of respondents disagreed with a single 30% recycled content

threshold. In these areas amongst others, respondents provided alternative

suggestions and further information for consideration.

11.4 For all areas of the tax design, the government will continue to consider

which approaches will best support the objectives of the tax, are most

administratively feasible and do not have a disproportionate impact on

business. HM Treasury will also continue to work closely with Defra to ensure

that the plastic packaging tax complements the reforms to the Packaging

Producer Responsibility regulations and proposals for consistent collection of

waste in England and a potential Deposit Return Scheme for drinks

containers.

11.5 The government will set out the next steps at Budget 2019. HMRC will

publish a technical consultation on the detail of the tax design at a later

date, and publish draft legislation for consultation in 2020.

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Annex A

List of respondents

A Plastic Planet Aerian Aggregate Industries UK Ltd Alliance for Beverage Cartons and the Environment Amcor Amey plc Anglian Water Services Ltd Antrim and Newtownabbey Borough Council Arc21 Ards and North Down Borough Council Association of Accounting Technicians Association of British HealthTech Industries Association of Directors of Environment, Economy, Planning & Transport Association of Manufacturers of Domestic Appliances Association of the British Pharmaceutical Industry Automatic Vending Association Basildon Borough Council Bedford Borough Council Benders Paper Cups Bericap UK Ltd Biffa Bio-based and Biodegradable Industries Association Birmingham City Council Blackburn with Darwen Borough Council Bolsover District Council Boots UK Borough of Pendle BPIF Cartons Braintree District Council British Beer & Pub Association British Brands Group British Generic Manufacturers Association British Plastics Federation British Retail Consortium British Soft Drinks Association British Toy & Hobby Association Britvic plc Broadland District Council Bryson Recycling Ltd Business In The Community Cambridge County Council Carlton Packaging Cast Metals Federation

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Castle Point Borough Council Celebration Paper & Plastics Ltd Central Bedfordshire Council Charpak Ltd Chartered Institute of Taxation Chartered Institution of Wastes Management Chemical Business Association CHEP UK Cheshire East Borough Council Cheshire West and Chester Council Chiltern, South Bucks and Wycombe District Councils City of Bradford Metropolitan District Council Company Chemists’ Association Comply Direct Ltd Co-op Group Cosmetic Toiletry & Perfumery Association Costa Coffee Council for Responsible Nutrition UK Coveris Cumbria County Council Dairy UK Danone UK&I David Rose Packaging Solutions Decorative Panels Group Delaware North UK Deloitte LLP Derbyshire County Council Devon Authorities Strategic Waste Committee Devon County Council Dover District Council and Folkestone & Hythe District Council Dow UK Ltd Dreamy Hollow Leisure Ltd DS Smith plc Durham County Council East London Waste Authority East Sussex County Council Ecosurety Ltd Elmbridge Borough Council Environmental Industries Commission Environment Links UK Environmental Packaging Solutions Environmental Policy Forum Environmental Services Association Epping Forest District Council Epsom & Ewell Borough Council Essex County Council Faerch UK Ltd Fareham Borough Council Fauna and Flora International FCC Environment Fermanagh and Omagh District Council Fidra Fluid Technology Generation Ltd Food and Drink Federation

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Foodservice Packaging Association Fresh Produce Consortium Frugalpac Ltd FuturEcoLogic Ltd Gaia Sustainable Retail Ltd GlaxoSmithKline Global Brands Ltd Gloucester City Council Grantham Centre for Sustainable Futures, University of Sheffield Greater London Authority Greater Manchester Combined Authority Green Alliance Greggs plc Guildford Borough Council Hampshire County Council Harlow Council Harrison Packaging Harrogate Spring Water Ltd Hertfordshire Waste Partnership Huhtamaki Iceland Foods Ltd IG Design Group UK Ltd Imerys Independent Packaging Environment and Safety Forum Industrial Packaging Association Industry Council for Packaging and the Environment Innocent Drinks Institute of Chartered Accountants in England and Wales Interlink Packaging (UK) Ltd International Meat Trade Association IVC Brunel Healthcare Ltd J Williams & Associates Japan Tobacco International Joint Trade Association Joint Waste Solutions KeCo Ltd Keep Britain Tidy Kent Resource Partnership Kettering Borough Council Kirklees Council Klöckner Pentaplast KM Packaging Services Ltd Law Society of Scotland Lechler Coatings Ltd Leeds City Council Leicester City Council Leicestershire County Council Lewes District and Eastbourne Borough Councils Lightweight Containers BV Lincolnshire County Council Lincolnshire Waste Partnership Lisburn & Castlereagh City Council Local Authority Recycling Advisory Committee Local Government Association

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London Borough of Haringey London Borough of Havering London Borough of Islington London Borough of Merton L'Oréal UKI Luton Borough Council Make UK Mars UK McDonald’s UK Medway Council Merseyside and Halton Waste Partnership Mid and East Antrim Borough Council Mole Valley District Council Molson Coors Brewing Company UK&I Monmouth Town Council Moores Furniture Group Ltd Muller UK&I LLP NACM CiderMakers Ltd National Association of Waste Disposal Officers National Office of Animal Health Ltd Natural England Natural Hydration Council Nestlé UK&I New Forest District Council Newcastle City Council Norfolk County Council Norfolk Waste Partnership North East Derbyshire District Council North London Waste Authority Nottinghamshire County Council Novamont S.p.A Ocado plc Orsted UK Oxford City Council Oxfordshire County Council Oxfordshire Environment Partnership Packaging Federation Packaging Scheme Forum PAGB Paper Cup Alliance Peterborough City Council Pippa Hill Sculpture Plastic Energy Ltd Plastic Oceans Foundation UK Plymouth City Council Policy Connect Polymer Processing Research Centre, Queen’s University Belfast Portsmouth City Council Potato Processors Association Ltd Premier Flexible Packaging Princes Limited Procter & Gamble Professional Publishers Association Project Integra

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Properpak Ltd Pura Velo Ltd Qeng Ho Ltd RH Smith & Sons (Wigmakers) Ltd Rainbow Cosmetics Rebel Kitchen RECOUP Recycle-Pak (Scotland) Ltd Recycling Technologies Reigate and Banstead Borough Council REPIC Ltd Resource Association Richmond and Wandsworth Councils Rotherham Metropolitan Borough Council Royal Borough of Kingston Upon Thames RPC Group plc RPC-BPI Recycled Products Rutland County Council Ryedale District Council Sainsbury's Supermarkets Ltd Sco-Fro Group Ltd Seda UK Ltd Sharp Interpack (Groupe Guillin) Sheffield City Council Smart Comply Social Style Ltd Sodexo Somerset Waste Partnership South Gloucestershire Council South Lakeland District Council South London Waste Partnership South Norfolk Council Southern Cross Packaging Ltd Staeger Clear Packaging Ltd SUEZ Recycling & Recovery UK Ltd Surfers Against Sewage Surrey Environment Partnership Surrey Heath Borough Council Synergy Compliance Ltd The Environment Exchange Tobacco Manufacturers Association Torbay Council Travis Perkins plc Trigon Snacks Trading Ltd UK Chemical Industries Association UK Environmental Law Association Unilever UK&I Urology Trade Association Valpak Ltd Vegware Viridor Vitacress Ltd Wastepack Ltd Way to Eco Ltd

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Wealden District Council West London Waste Authority Whitbread plc Woking Borough Council WRAP WYG Wyre Council Your Ideal Business Partner Zip-Pak (ITW UK Ltd) The government also received responses from 123 individuals and community groups who responded in a private capacity.

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HM Treasury contacts

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If you require this information in an alternative format or have

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